CN108609733B - Device and method for retarding sludge calcification by IC anaerobic reactor - Google Patents

Device and method for retarding sludge calcification by IC anaerobic reactor Download PDF

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CN108609733B
CN108609733B CN201810603235.8A CN201810603235A CN108609733B CN 108609733 B CN108609733 B CN 108609733B CN 201810603235 A CN201810603235 A CN 201810603235A CN 108609733 B CN108609733 B CN 108609733B
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partition plate
gas
air
pipe
anaerobic reactor
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CN108609733A (en
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郑平
陈文达
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Zhejiang University ZJU
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Zhejiang University ZJU
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/28Anaerobic digestion processes
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/14Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
    • B01D53/1456Removing acid components
    • B01D53/1475Removing carbon dioxide
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/14Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols by absorption
    • B01D53/18Absorbing units; Liquid distributors therefor
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/28Anaerobic digestion processes
    • C02F3/2866Particular arrangements for anaerobic reactors
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/28Anaerobic digestion processes
    • C02F3/2866Particular arrangements for anaerobic reactors
    • C02F3/2873Particular arrangements for anaerobic reactors with internal draft tube circulation
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

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  • Life Sciences & Earth Sciences (AREA)
  • Chemical & Material Sciences (AREA)
  • Microbiology (AREA)
  • Engineering & Computer Science (AREA)
  • Water Supply & Treatment (AREA)
  • Environmental & Geological Engineering (AREA)
  • Hydrology & Water Resources (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Organic Chemistry (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Treating Waste Gases (AREA)
  • Treatment Of Sludge (AREA)

Abstract

The invention discloses a device and a method for retarding sludge calcification by an IC anaerobic reactor. The device comprises an exhaust box, an air compressor, a carbon dioxide absorber and a gas distribution pipe, and the components are connected into a whole by the gas distribution pipe. The invention adopts the modes of upper end air extraction and lower end air lifting to accelerate methane generated in the reaction chamber to enter the lifting pipe, and reduce the carbon dioxide concentration on the surface of sludge in the reaction chamber, thereby reducing the generation of calcium salt precipitation and relieving calcification and inactivation of granular sludge.

Description

Device and method for retarding sludge calcification by IC anaerobic reactor
Technical Field
The invention belongs to the field of organic wastewater treatment, and particularly relates to a device and a method for retarding sludge calcification by an IC anaerobic reactor.
Background
IC (Internal Circulation) anaerobic reactor, also called internal circulation anaerobic reactor, is a high-efficiency anaerobic reactor, which consists of an upper reaction chamber and a lower reaction chamber. The top of the upper reaction chamber is provided with a gas-liquid separator, the upper part of the upper reaction chamber is provided with an upper three-phase separator, and the upper three-phase separator is connected with a second riser. The upper part of the lower reaction chamber is provided with a lower three-phase separator which is connected with a first lifting pipe. The bottom of the lower reaction chamber is also provided with a water distributor, the water distributor is connected with the lower end of a return pipe, and the upper end of the return pipe is positioned below the gas-liquid separator.
The water inlet pipe outside the reactor stretches into the bottom of the reaction chamber and is communicated with the water distributor, the organic wastewater entering from the water distributor is mixed with sludge, microorganisms in the sludge decompose organic matters to generate biogas, and the generated biogas has a good stirring effect on the reaction liquid. Biogas rises into the riser and carries a part of fermentation liquor into the gas-liquid separator during the rising process. After the biogas enters the lifting pipe, the density of the fermentation liquid in the lifting pipe is reduced, and density difference is generated between the biogas and the main fermentation liquid with higher density. This density difference drives the fermentation broth to be continuously lifted into the gas-liquid separator at the top, thereby realizing continuous internal circulation of the fermentation broth. After the biogas and the fermentation liquor carried by the biogas reach the gas-liquid separator, the biogas rises and is discharged, and the fermentation liquor returns to the lower reaction chamber through the return pipe under the action of gravity, so that the rising water flow speed of the IC anaerobic reactor is increased.
However, when an IC anaerobic reactor is used to treat high hardness organic wastewater such as papermaking wastewater, a large amount of Ca is present in the wastewater 2+ Ions, which are very likely to produce calcium carbonate precipitates after encountering carbon dioxide generated by the sludge, are mostly precipitated on the surface of the sludge. Over time, excessive precipitated substances accumulate on the surface of the sludge, causing calcification of the granular sludge, thereby weakening the activity of the sludge and shortening the service life of the sludge. Since the biogas yield in the lower reaction chamber of the IC anaerobic reactor accounts for the vast majority of the overall biogas yield, the sludge calcification reaction mainly occurs in the lower reaction chamber.
Disclosure of Invention
The invention aims to solve the problem of calcification of granular sludge in an IC anaerobic reactor and provides a device and a method for slowing down calcification of sludge in the IC anaerobic reactor.
The specific technical scheme adopted by the invention is as follows:
an IC anaerobic reactor sludge calcification slowing device is arranged in the IC anaerobic reactor and comprises an exhaust box, an air compressor, a carbon dioxide absorber, a gas pipe and a gas distribution pipe;
the exhaust box shell is in a bottomless cuboid shape, a side wall is surrounded by two longitudinal partition plates and two transverse partition plates, and a cover plate is arranged at the top of the exhaust box shell to be airtight; an inner member is arranged in the exhaust box shell, the inner member comprises a plurality of partition boards, a separation chamber which is in an inverted funnel shape is arranged between two transverse partition boards of the exhaust box shell, the top of the separation chamber is open and communicated with the inner headspace of the exhaust box, an air outlet chamber with the bottom communicated with the inner headspace of the exhaust box is arranged at a cover plate right above the separation chamber, and a circulation channel is reserved between two sides of the separation chamber and the exhaust box shell; the left-side first-stage inclined partition plate and the right-side first-stage inclined partition plate serving as two inclined bottom edges of the separation chamber are not connected, the right-side first-stage inclined partition plate is longer than the left-side first-stage inclined partition plate, a second-stage inclined partition plate is arranged below the right-side first-stage inclined partition plate in parallel and is clamped between the two inclined partition plates to form a diagonal cutting channel, the bottom of the left-side first-stage inclined partition plate is connected with a stepped partition plate, the stepped partition plate is sequentially connected with a first partition plate section, a second partition plate section, a third partition plate section and a fourth partition plate section to form a continuous W shape, the first partition plate section and the third partition plate section are respectively parallel to the right-side first-stage inclined partition plate and the second partition plate, water leakage gaps are reserved between the right-side first-stage inclined partition plate and the second partition plate section and between the second-stage inclined partition plate and the fourth partition plate section, and the stepped partition plate, and the right-side first-stage inclined partition plate and the second-stage inclined partition plate form a three-way channel; the bottom of the separation chamber is communicated with the inner cavity of the extraction box through the three-way channel;
the air exhaust box is arranged in the gas-liquid separator at the top of the anaerobic reactor, the air compressor and the carbon dioxide absorber are arranged outside the anaerobic reactor, and the air distribution pipe is arranged in the water distribution area at the bottom of the anaerobic reactor; the air outlet chamber of the air extraction box is connected with the inlet of the air compressor through an air outlet pipe, and the outlet of the air compressor is sequentially connected with the carbon dioxide absorber and the air distribution pipe through an air transmission pipe.
Optionally, the upper middle part of the carbon dioxide absorber is a gas chamber, the lower middle part is an absorption liquid storage tank, and a purified gas output pipe and an absorption liquid supplementing pipe are arranged at the top of the gas chamber; the shell side wall of the carbon dioxide absorber is provided with a mixed gas input pipe and an absorption liquid discharge pipe, the mixed gas input pipe and the absorption liquid discharge pipe extend into the shell side wall, then are bent vertically downwards, and the pipeline outlets are all located below the liquid level of the absorption liquid storage tank.
Optionally, the ratio of the volume of the exhaust box to the volume of the IC anaerobic reactor is 1:1000; length of the extraction box: width: the height ratio is 2:1: and 1, the height of the air outlet chamber is 1/3 of that of a longitudinal partition plate of the air extraction box.
Optionally, in the air extraction box, the width of the water leakage gap is 20-40 mm; the width of the inclined cutting channel between the right first-stage inclined partition plate and the second-stage inclined partition plate is 50-150 mm.
Optionally, the ratio of the volume of the carbon dioxide absorber to the volume of the IC anaerobic reactor is 1:25, a step of selecting a specific type of material; the height-to-diameter ratio of the carbon dioxide absorber is 3:1.
optionally, the gas distribution pipe is formed by a plurality of gas distribution branch pipes, is in a dendritic shape with the center outwards expanded, is distributed at the bottom of the anaerobic reactor, and is alternately perforated downwards on the gas distribution branch pipes, and the inclination angle between the perforation and the horizontal plane is 45 degrees.
Optionally, the air outlet chamber consists of two longitudinal partition boards, and the two longitudinal partition boards are arranged between two transverse partition boards of the air extraction box shell to enclose the side wall of the air outlet chamber; the top of the air outlet chamber is sealed, and the bottom of the air outlet chamber extends into the separation chamber.
Optionally, the top of the separation chamber is above the gas-liquid interface 23 in the operating state of the gas-liquid separator.
Optionally, in the three-way channel, the first channel is formed by clamping the first partition plate section, the second partition plate section and the second inclined partition plate, the second channel is formed by clamping the third partition plate section, the fourth partition plate section and the second inclined partition plate, and the third channel is a tangential inclined channel between the right first inclined partition plate and the second inclined partition plate; the three channels are communicated with each other at the bottommost end of the secondary inclined partition board.
Another object of the present invention is to provide a granular sludge calcification slowing process using the above device, which comprises the following steps:
firstly, normally operating an IC anaerobic reactor, starting an air compressor to continuously exhaust the exhaust box, keeping a negative pressure state in the exhaust box, and enabling gas and liquid at the lower part of the exhaust box to move upwards and enabling part of liquid carried by the gas to enter the separation chamber from the top; in the separation chamber, liquid moves downwards under the action of gravity to enter the three-way channel, and in the process of the movement of the liquid, the liquid at the lower part of the three-way channel is pressed by utilizing kinetic energy converted from potential energy to enter the three-way channel upwards, so that the imbalance of air pressure in the air extraction box is maintained, and the air extraction function of the air extraction box is realized; the gas entering the three-way channel is discharged through the inclined cutting channel between the first-stage inclined baffle plate and the second-stage inclined baffle plate on the right side under the action of pressure difference; the gas in the separation chamber is continuously sucked by the air compressor and is discharged out of the anaerobic reactor from the air outlet chamber, part of the sucked gas is sent into the carbon dioxide absorber through the gas pipe, carbon dioxide is removed in the carbon dioxide absorber, and then the purified gas is input into the gas distribution pipe through the gas pipe; purified gas passing clothThe gas pipe enters the lower reaction chamber of the IC anaerobic reactor to push the methane in the lower reaction chamber to move upwards, and the methane generated in the lower reaction chamber rapidly enters the upper part of the gas-liquid separator through the lifting pipe under the combined action of the pumping of the methane by the upper end pumping box and the lifting of the methane by the lower end purifying gas, so that the CO on the surface of the sludge in the lower reaction chamber is reduced 2 Concentration, inhibit the occurrence of precipitation reaction and slow down the calcification of granular sludge.
The invention not only can reduce the concentration of carbon dioxide in the reaction chamber and effectively relieve the problem of sludge calcification of the anaerobic reactor when treating high-hardness organic wastewater, but also can accelerate the internal circulation of the anaerobic reactor, further increase the rising water flow rate of the anaerobic reactor and be beneficial to enhancing the load impact resistance of the anaerobic reactor; in addition, the mixed gas generated in the anaerobic reactor is partially refluxed, so that the mixing of the sludge and the inlet water in the reaction chamber can be promoted, and the degradation rate of the granular sludge on the organic matters is improved.
Drawings
The drawings are intended to illustrate and explain the invention and are not intended to limit the scope of the invention.
FIG. 1 is a schematic view of the whole of the present invention installed in an anaerobic reactor;
FIG. 2 is a schematic view of the internal structure of the suction box;
FIG. 3 is a three-dimensional schematic view of the internal structure of the exhaust box (the right side of the cover plate on the top of the exhaust box housing and the cover plate on the top of the air outlet chamber are omitted for simplicity in the drawing);
FIG. 4 is a schematic diagram of the carbon dioxide absorber;
fig. 5 is a schematic view of the gas distribution pipe.
In the figure: the lower reaction chamber 1, the upper reaction chamber 2, the lower three-phase separator 3, the upper three-phase separator 4, the first riser 5, the suction box 6, the gas outlet pipe 7, the air compressor 8, the gas delivery pipe 9, the carbon dioxide absorber 10, the gas distribution pipe 11, the water inlet pipe 12, the water distributor 13, the return pipe 14, the second riser 15, the gas-liquid separator 16, the right-side first-stage inclined partition 17, the first partition section 18, the second-stage inclined partition 19, the third partition section 20, the water leakage slit 21, the gas outlet chamber 22, the gas-liquid interface 23, the liquid movement direction 24, the gas movement direction 25, the gas-liquid mixture movement direction 26, the longitudinal partition 27, the inner member longitudinal partition 28, the left-side first-stage inclined partition 29, the cover plate 30, the diaphragm 31, the separation chamber 32, the gas chamber 33, the absorption liquid storage tank 34, the purified gas outlet pipe 35, the absorption liquid replenishing pipe 36, the mixed gas inlet pipe 37, the absorption liquid discharge pipe 38, the liquid movement direction 39 in the carbon dioxide absorber, the gas flow direction 40 in the carbon dioxide absorber, and the gas distribution branch pipes 41 and the ventilation holes 42.
Detailed Description
The invention is further illustrated and described below with reference to the drawings and detailed description. The technical features of the embodiments of the invention can be combined correspondingly on the premise of no mutual conflict.
The invention provides an IC anaerobic reactor sludge calcification slowing device which is arranged in the IC anaerobic reactor. The IC anaerobic reactor may be of a conventional structure, and in this embodiment, the structure of the IC anaerobic reactor is shown in fig. 1, which is an overall schematic diagram after the device is installed in the anaerobic reactor. The IC anaerobic reactor comprises an upper reaction chamber and a lower reaction chamber, a gas-liquid separator 16 is arranged at the top outside the upper reaction chamber 2, an upper three-phase separator 4 is arranged at the upper part of the upper reaction chamber 2, and the upper three-phase separator 4 is connected with a second riser 15. The upper part of the lower reaction chamber 1 is provided with a lower three-phase separator 3, and the lower three-phase separator 3 is connected with a first riser 5. The first riser pipe 5 and the second riser pipe 15 are both connected to a gas-liquid separator 16, a water distributor 13 is further arranged at the bottom of the lower reaction chamber 1, the water distributor 13 is connected with the lower end of a return pipe 14, and the upper end of the return pipe 14 is connected with the bottom of the gas-liquid separator 16. The water inlet pipe 12 outside the reactor stretches into the bottom of the lower reaction chamber 1 and is communicated with the water distributor 13, the organic wastewater entering from the water distributor 13 is mixed with sludge, microorganisms in the sludge decompose organic matters to generate biogas, and the generated biogas has a good stirring effect on the reaction liquid. Biogas rises into the first riser pipe 5 and the second riser pipe 15 and carries a part of the fermentation broth during the rising process into the gas-liquid separator 16. After the biogas enters the lifting pipe, the density of the fermentation liquid in the lifting pipe is reduced, and density difference is generated between the biogas and the main fermentation liquid with higher density. This density difference drives the fermentation broth to be continuously lifted into the top gas-liquid separator 16, thereby achieving continuous internal circulation of the fermentation broth. After the biogas and the fermentation liquor carried by the biogas reach the gas-liquid separator 16, the biogas rises and is discharged, and the fermentation liquor sinks to the lower part of the gas-liquid separator 16 and returns to the lower reaction chamber 1 through the return pipe 14 under the action of gravity, so that the rising water flow speed of the IC anaerobic reactor is increased. However, when high-hardness organic wastewater is treated, sludge calcification is easy to occur in the lower reaction chamber, so that the sludge calcification slowing device is required to be used for treatment.
The device for reducing sludge calcification comprises an exhaust box 6, an air compressor 8, a carbon dioxide absorber 10, an air delivery pipe 9 and an air distribution pipe 11, wherein the air delivery pipe 9 connects the components into a whole.
The schematic diagram of the internal structure of the extraction box is shown in fig. 2, and the three-dimensional schematic diagram of the internal structure of the extraction box is shown in fig. 3. The outer shell of the extraction box 6 is in a bottomless cuboid shape, two longitudinal partition plates 27 and two transverse partition plates 31 enclose a side wall, and a cover plate 30 is arranged at the top and is airtight. The volume ratio of the exhaust box 6 to the IC anaerobic reactor is 1:1000; length of the suction box 6: width: the height ratio is 2:1:1. the inner member is arranged in the outer shell of the extraction box 6, and comprises two inner member longitudinal partition plates 28, a right-side first-stage inclined partition plate 17 and a left-side first-stage inclined partition plate 29, wherein the lengths of all partition plates (namely the length direction shown in fig. 3) are the same as those of the longitudinal partition plates 27, namely the two ends of the partition plates of the inner member are respectively and tightly connected with the transverse partition plates 31. The inner member separates a separating chamber 32 in the shape of an inverted funnel between two diaphragm plates 31 of the outer shell of the extraction box 6, and the upper part of the longitudinal section of the inner member is a cuboid, and the lower part of the inner member is an inverted trapezoid. The top of the separation chamber 32 is open and is communicated with the inner headspace of the extraction box 6, the cover plate 30 right above the separation chamber 32 is provided with an air outlet chamber 22, the bottom of which is communicated with the inner headspace of the extraction box 6, the air outlet chamber is enclosed by two transverse partition plates and longitudinal partition plates to form a side wall, the top of the air outlet chamber is airtight and extends out of the cover plate 30, the bottom of the air outlet chamber is not provided with a bottom plate, and the air outlet chamber extends into the separation chamber 32 and is positioned above the liquid level. The air outlet chamber 22 and the cover plate 30 are still kept airtight. The height of the air outlet chamber 22 is 1/3 of the height of the longitudinal partition 27 of the suction box 6. The top of the separation chamber 32 is higher than the gas-liquid interface 23 in the operation state of the gas-liquid separator 16, a circulation channel is reserved between the two sides of the separation chamber 32 and the outer shell of the extraction box 6, so that the gas-liquid mixture at the two sides flows upwards, and part of the gas-liquid mixture passes over the inner member longitudinal baffle plate 28 and then enters the separation chamber 32. The left-side first-stage inclined partition plate 29 and the right-side first-stage inclined partition plate 17 serving as two inclined bottom edges of the separation chamber 32 are not connected, and a gap is reserved between the two. The right-side one-level inclined baffle 17 is longer than the left-side one-level inclined baffle 29, a second-level inclined baffle 19 is arranged below the right-side one-level inclined baffle 17 in parallel, a cutting inclined channel is formed by clamping the two inclined baffles, the bottom of the left-side one-level inclined baffle 29 is connected with a stepped baffle, the stepped baffle is formed by sequentially connecting a first baffle section 18, a second baffle section, a third baffle section 20 and a fourth baffle section, the first baffle section 18 and the third baffle section 20 are respectively parallel to the right-side one-level inclined baffle 17 and the second-level inclined baffle 19, the first baffle section is perpendicular to the left-side one-level inclined baffle 29, and the third baffle section is parallel to the first baffle section. Water leakage gaps 21 are reserved between the right-side first-stage inclined baffle 17 and the second baffle section and between the second-stage inclined baffle 19 and the fourth baffle section, and the width of the water leakage gaps 21 is 20-40 mm; the width of the tangential inclined channel between the right primary inclined baffle 17 and the second inclined baffle 19 is 50-150 mm. The stepped diaphragm and the secondary inclined diaphragm 19 are also the same in length as the longitudinal diaphragm 27, i.e. the two ends of the diaphragm are respectively and closely connected with the diaphragm 31, and the diaphragm 31 is shared.
The stepped partition plate, the right-side first-stage inclined partition plate 17 and the second-stage inclined partition plate 19 form a three-way passage. The bottom of the separation chamber 32 is communicated with the inner cavity of the extraction box 6 through the three-way passage. In the three-way channel, a first channel is formed by clamping a first partition plate section 18, a second partition plate section and a second-stage inclined partition plate 19, a second channel is formed by clamping a third partition plate section 20, a fourth partition plate section and the second-stage inclined partition plate 19, and the third channel is an inclined cutting channel between the right-side first-stage inclined partition plate 17 and the second-stage inclined partition plate 19. The first channel and the second channel are connected into a ladder-type channel, and the three channels are communicated in a crossing way at the bottommost end of the secondary inclined partition plate 19. The three-way channel can ensure that liquid in the separation zone smoothly flows downwards, and gas and liquid below the three-way channel can not directly enter the separation zone.
When the suction box 6 is installed in the anaerobic reactor and operates normally, the liquid movement direction 24, the gas movement direction 25 and the gas-liquid mixture movement direction 26 therein are shown in fig. 2. When the device operates, due to the operation of the air compressor 8 connected behind the air outlet chamber 22, the air pressure near the air outlet chamber 22 in the air extraction box 6 is smaller, the air and the liquid at the lower part of the air extraction box are promoted to move upwards, and due to a certain height difference between the assumed air-liquid interface 23 and the upper end of the inner member longitudinal partition plate 28, only part of the liquid in the upward moving air-liquid can enter the separation chamber 32 together with the air, and the movement direction of the two is shown as the movement direction 26 of the air-liquid mixture. Within separation chamber 32, the gas is drawn and exhausted from outlet chamber 22, while the liquid moves downward due to gravity. In the motion process, the potential energy of the liquid is converted into kinetic energy, the upward flowing trend of the fluid at the lower part of the two stages of steps is pressed, the fluid at the steps is kept in a downward flowing state, the air pressure imbalance in the air extraction box is maintained, and the air extraction box is used for extracting air. In order to ensure the downward movement of the liquid entering the separation chamber, a two-stage ladder structure is specially arranged, and the width of the water leakage gap is controlled to be 20-40 mm. In addition, in order to avoid the situation that the gas is accumulated in the ladder and cannot be discharged to block the ladder, the secondary inclined baffle plate 19 and the right primary inclined baffle plate 17 are not in airtight connection, so that the gas entering the ladder can be discharged through a channel between the right primary inclined baffle plate 17 and the secondary inclined baffle plate 19 under the action of pressure difference.
The air exhaust box 6 is arranged in a gas-liquid separator 16 at the top of the anaerobic reactor, the air compressor 8 and the carbon dioxide absorber 10 are arranged outside the anaerobic reactor, and the air distribution pipe 11 is arranged in a water distribution area at the bottom in the anaerobic reactor; the air outlet chamber 22 of the air extraction box 6 is connected with the inlet of the air compressor 8 through the air outlet pipe 7, and the outlet of the air compressor 8 is sequentially connected with the carbon dioxide absorber 10 and the air distribution pipe 11 through the air transmission pipe 9.
Specifically, when the anaerobic reactor is treating high hardness organic wastewater, the lower reaction chamber 1 generates a large amount of biogas, which continuously rises and enters the first riser 5 while carrying a part of the fermentation broth through the first riser 5 into the gas-liquid separator 16 at the top of the anaerobic reactor. When the air compressor 8 of the device is started, the air at the upper part of the air-liquid separator 16 is accelerated to be pumped out by the air pumping box 6, so that the air pressure at the upper part of the air-liquid separator 16 is reducedPromote the lifting of the biogas in the lower reaction chamber 1. The liquid in the gas-liquid separator 16 cannot enter the air outlet pipe due to the structural design of the air extraction box 6, and flows back to the lower reaction chamber 1 through the return pipe 14 under the action of gravity. And (3) sending part of the extracted mixed gas into a carbon dioxide absorber 10 through a gas pipe 9, removing carbon dioxide in the carbon dioxide absorber 10, and then inputting purified gas into a gas distribution pipe 11 through the gas pipe 9, wherein the purified gas enters a lower reaction chamber through the gas distribution pipe 11 to push methane in the lower reaction chamber 1 to move upwards. In summary, under the combined action of the suction of the biogas by the upper-end suction box 6 and the lifting of the biogas by the lower-end purified gas, the biogas generated in the reaction chamber 1 can rapidly enter the upper part of the gas-liquid separator 16 through the first lifting pipe 5, thereby reducing CO on the surface of the sludge in the lower reaction chamber 1 2 Concentration, inhibit the occurrence of precipitation reaction, thereby effectively relieving the calcification problem of sludge.
In addition, the invention can reduce the concentration of carbon dioxide in the reaction chamber, effectively relieve the problem of sludge calcification of the anaerobic reactor when treating high-hardness organic wastewater, and can accelerate the internal circulation of the anaerobic reactor because part of fermentation liquor is carried in the gas rising process, thereby further increasing the rising water flow rate of the anaerobic reactor and being beneficial to the load impact resistance of the anaerobic reactor; and the mixed gas generated in the anaerobic reactor is partially refluxed, so that the mixing of the sludge and the inlet water in the reaction chamber can be promoted, and the degradation rate of the granular sludge on organic matters is improved.
The carbon dioxide absorber according to the present invention is structured as shown in fig. 4. The carbon dioxide absorber 10 is connected with the air extraction box 6 through the air pipe 9, the carbon dioxide absorber 10 is cylindrical, and the height-diameter ratio is 3:1, the ratio of the volume of the anaerobic reactor to the volume of the IC anaerobic reactor is 1:25. the carbon dioxide absorber is equally divided into an upper part, a middle part and a lower part, wherein the upper part is a gas chamber 33, and the middle part and the lower part are absorption liquid storage tanks 34; the top of the air chamber is provided with a purified gas output pipe 35 and an absorption liquid supplementing pipe 36; the gas mixture input pipe 37 extends into the center of the cylinder from the side wall of the shell between the upper part and the middle part of the cylinder, is vertically bent downwards and extends between the middle part and the lower part of the cylinder; an absorption liquid discharge pipe 38 is provided opposite the mixture inlet pipe of the cylinder, and extends from the side wall of the housing into the center of the cylinder, is bent vertically downward, and extends to a level half of the center of the cylinder. The outlets of the mixture gas input pipe 37 and the absorption liquid discharge pipe 38 are located below the liquid surface of the absorption liquid reservoir 34. The direction of liquid movement 39 in the carbon dioxide absorber and the direction of gas flow 40 in the carbon dioxide absorber are respectively marked in the figure. When the device is in operation, the mixed gas enters the mixed gas input pipe through the gas pipe 9 and is sent into the absorption liquid storage tank to fully react with the absorption liquid in the mixed gas, and the mixed gas rises after the reaction and is output from the purified gas output pipe 35. The absorption liquid in the carbon dioxide absorber can be supplemented through the absorption liquid supplementing pipe or discharged through the absorption liquid discharging pipe, so that the regeneration of the absorption liquid is realized.
Further, as shown in fig. 5, the gas distribution pipe 41 according to the present invention is connected to the carbon dioxide absorber 10 via the gas pipe 9. The gas distribution pipe 11 is composed of a plurality of gas distribution branch pipes 41, the gas distribution branch pipes 41 are distributed at the bottom of the anaerobic reactor in a dendritic shape which expands outwards from the center, the gas distribution pipe alternately penetrates through the gas holes 42 downwards, and the inclination angle of the gas holes 42 and the horizontal plane is 45 degrees. The purified gas enters the gas distribution branch pipe 41 through the gas pipe 9 and then is discharged downwards through the vent hole. Because the inclination angle of the vent hole 42 and the horizontal plane is 45 degrees, the vent hole can stir the fermentation liquid in the lower reaction chamber 1 while ventilating, and the removal rate of sludge in the reaction chamber to organic matters is improved.
In addition, in order to ensure the safety of the device in the operation process, the gas pipes adopted by the invention meet the requirements of GB-T20801-2006 pressure pipeline standard industrial pipeline.
The granular sludge calcification slowing process based on the device comprises the following steps:
according to the conventional operation process, the IC anaerobic reactor is normally operated, the air compressor 8 is started to continuously exhaust the air suction box 6, the negative pressure state in the air suction box 6 is maintained, the air and the liquid at the lower part of the air suction box 6 are promoted to move upwards, and part of the liquid carried by the air enters the separation chamber 32 from the top; the liquid moves downwards in the separation chamber 32 by gravity into said three-way channel and during the movement of the liquid presses the lower part of the three-way channel by means of kinetic energy converted from potential energyThe liquid in the suction box 6 is kept unbalanced in air pressure, so that the suction function of the suction box 6 on the air is realized; the gas entering the three-way channel is discharged through the inclined cutting channel between the right first-stage inclined baffle plate 17 and the second-stage inclined baffle plate 19 under the action of pressure difference; the gas in the separation chamber 32 is continuously sucked by the air compressor 8 and discharged out of the anaerobic reactor from the air outlet chamber 22, part of the sucked gas is sent into the carbon dioxide absorber 10 through the gas pipe 9, carbon dioxide is removed in the carbon dioxide absorber 10, and then purified gas is input into the gas distribution pipe 11 through the gas pipe 9; the purified gas enters the lower reaction chamber 1 of the IC anaerobic reactor through the gas distribution pipe 11 to push the methane in the lower reaction chamber 1 to move upwards, and under the combined action of the pumping of the methane by the upper end pumping box 6 and the lifting of the methane by the purified gas at the lower end, the methane generated in the lower reaction chamber 1 rapidly enters the upper part of the gas-liquid separator 16 through the lifting pipe, thereby reducing the CO on the surface of the sludge in the lower reaction chamber 1 2 Concentration, inhibit the occurrence of precipitation reaction and slow down the calcification of granular sludge.
The above embodiment is only a preferred embodiment of the present invention, but it is not intended to limit the present invention. Various changes and modifications may be made by one of ordinary skill in the pertinent art without departing from the spirit and scope of the present invention. Therefore, all the technical schemes obtained by adopting the equivalent substitution or equivalent transformation are within the protection scope of the invention.

Claims (8)

1. An IC anaerobic reactor sludge calcification slowing device is characterized by comprising an exhaust box (6), an air compressor (8), a carbon dioxide absorber (10), a gas pipe (9) and a gas distribution pipe (11);
the outer shell of the air extraction box (6) is in a bottomless cuboid shape, two longitudinal partition plates (27) and two transverse partition plates enclose a side wall, and a cover plate (30) is arranged at the top of the air extraction box to be airtight; an inner member is arranged in the shell of the air extraction box (6), the inner member comprises a plurality of partition boards, a separation chamber (32) which is in an inverted funnel shape is arranged between two transverse partition boards of the shell of the air extraction box (6), the top of the separation chamber (32) is open and communicated with the inner top of the air extraction box (6), an air outlet chamber (22) with the bottom communicated with the inner top of the air extraction box (6) is arranged at a cover plate (30) right above the separation chamber (32), and a circulation channel is reserved between two sides of the separation chamber (32) and the shell of the air extraction box (6); the left-side first-stage inclined partition plate (29) and the right-side first-stage inclined partition plate (17) serving as two inclined bottom edges of the separation chamber (32) are not connected, the right-side first-stage inclined partition plate (17) is longer than the left-side first-stage inclined partition plate (29), a second-stage inclined partition plate (19) is arranged below the right-side first-stage inclined partition plate (17) in parallel, a tangential inclined channel is clamped between the two inclined partition plates, the bottom of the left-side first-stage inclined partition plate (29) is connected with a stepped partition plate, the stepped partition plate is formed by sequentially connecting a first partition plate section (18), a second partition plate section, a third partition plate section (20) and a fourth partition plate section to form a continuous W-shaped structure, the first partition plate section (18) and the third partition plate section (20) are respectively parallel to the right-side first-stage inclined partition plate (17) and the second-stage inclined partition plate (19), water leakage gaps (21) are reserved between the right-side first-stage inclined partition plate (17) and the second-stage inclined partition plate section and between the second-stage inclined partition plate section and a three-way channel is reserved between the second-stage inclined partition plate section and the second-stage inclined partition plate section (19) respectively; the bottom of the separation chamber (32) is communicated with the inner cavity of the extraction box (6) through the three-way channel; the top of the separation chamber (32) is higher than a gas-liquid interface (23) of the gas-liquid separator (16) in the operation state;
in the three-way channel, a first channel is formed by clamping the first partition plate section (18), a second partition plate section and a second-stage inclined partition plate (19), a second channel is formed by clamping the third partition plate section (20), a fourth partition plate section and the second-stage inclined partition plate (19), and the third channel is an inclined cutting channel between the right-side first-stage inclined partition plate (17) and the second-stage inclined partition plate (19); the three channels are communicated with each other at the bottom end of the secondary inclined partition plate (19);
the air exhaust box (6) is arranged in the gas-liquid separator (16) at the top of the anaerobic reactor, the air compressor (8) and the carbon dioxide absorber (10) are arranged outside the anaerobic reactor, and the air distribution pipe (11) is arranged in the water distribution area at the bottom in the anaerobic reactor; the air outlet chamber (22) of the air extraction box (6) is connected with the inlet of the air compressor (8) through the air outlet pipe (7), and the outlet of the air compressor (8) is sequentially connected with the carbon dioxide absorber (10) and the air distribution pipe (11) through the air transmission pipe (9).
2. The IC anaerobic reactor sludge calcification slowing device according to claim 1, wherein the upper middle part of the carbon dioxide absorber (10) is a gas chamber (33), the lower middle part is an absorption liquid storage tank (34), and a purified gas output pipe (35) and an absorption liquid supplementing pipe (36) are arranged at the top of the gas chamber (33); the shell side wall of the carbon dioxide absorber (10) is provided with a mixed gas input pipe (37) and an absorption liquid discharge pipe (38), the mixed gas input pipe (37) and the absorption liquid discharge pipe (38) extend into the shell side wall, then are bent vertically downwards, and pipeline outlets are all located below the liquid level of the absorption liquid storage tank (34).
3. An IC anaerobic reactor sludge calcification slowing device according to claim 1, characterized in that the ratio of the volume of the suction box (6) to the IC anaerobic reactor is 1:1000; length of the extraction box (6): width: the height ratio is 2:1:1, the height of the air outlet chamber (22) is 1/3 of the longitudinal partition plate (27) of the air extraction box (6).
4. The IC anaerobic reactor sludge calcification slowing device according to claim 1, wherein in the air extraction box (6), the width of the water leakage gap (21) is 20-40 mm; the width of the inclined cutting channel between the right primary inclined partition plate (17) and the second inclined partition plate (19) is 50-150 mm.
5. The IC anaerobic reactor sludge calcification slowing device as claimed in claim 1, wherein the ratio of the volume of the carbon dioxide absorber (10) to the IC anaerobic reactor is 1:25, a step of selecting a specific type of material; the aspect ratio of the carbon dioxide absorber (10) is 3:1.
6. the IC anaerobic reactor sludge calcification slowing device according to claim 1, wherein the gas distribution pipe (11) is composed of a plurality of gas distribution branch pipes (41) in a dendritic shape expanding outwards from the center, the gas distribution pipe (11) is distributed at the bottom of the anaerobic reactor, the gas distribution branch pipes (41) are alternately perforated downwards, and the inclination angle of the perforation and the horizontal plane is 45 degrees.
7. The IC anaerobic reactor sludge calcification slowing device according to claim 1, wherein the air outlet chamber (22) is composed of two longitudinal partition boards, the two longitudinal partition boards are arranged between two transverse partition boards of the outer shell of the air extraction box (6), and the side wall of the air outlet chamber (22) is defined; the top of the air outlet chamber (22) is sealed, and the bottom of the air outlet chamber extends into the separation chamber (32).
8. A granular sludge calcification mitigation process using the apparatus of claim 1, characterized by the steps of:
the IC anaerobic reactor is normally operated, an air compressor (8) is started to continuously exhaust the air suction box (6), the negative pressure state in the air suction box (6) is maintained, the air and the liquid at the lower part of the air suction box (6) are driven to move upwards, and part of the liquid carried by the air enters the separation chamber (32) from the top; in the separation chamber (32), liquid moves downwards under the action of gravity into the three-way channel, and in the process of the movement of the liquid, the liquid at the lower part of the three-way channel is pressed by utilizing kinetic energy converted from potential energy to upwards enter the three-way channel, so that the imbalance of air pressure in the air extraction box (6) is maintained, and the air extraction function of the air extraction box (6) is realized; the gas entering the three-way channel is discharged through a tangential inclined channel between the right primary inclined baffle plate (17) and the second inclined baffle plate (19) under the action of pressure difference; the gas in the separation chamber (32) is continuously sucked by the air compressor (8) and discharged out of the anaerobic reactor from the air outlet chamber (22), part of the sucked gas is sent into the carbon dioxide absorber (10) through the gas pipe (9), carbon dioxide is removed in the carbon dioxide absorber (10), and then the purified gas is input into the gas distribution pipe (11) through the gas pipe (9); the purified gas enters a lower reaction chamber (1) of the IC anaerobic reactor through a gas distribution pipe (11) to push methane in the lower reaction chamber (1) to move upwards, and the methane is pumped into an upper end pumping box (6)Under the combined action of the suction of the gas and the lifting of the lower-end purified gas on the biogas, the biogas generated in the lower reaction chamber (1) can quickly enter the upper part of the gas-liquid separator (16) through the lifting pipe, thereby reducing the CO on the surface of the sludge in the lower reaction chamber (1) 2 Concentration, inhibit the occurrence of precipitation reaction and slow down the calcification of granular sludge.
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